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EC number: 216-613-3 | CAS number: 1624-62-0
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Endpoint summary
Administrative data
Description of key information
local lymph node assay: not skin sensitizing (van Otterdijk, 2011); read-across from Estrone
Key value for chemical safety assessment
Skin sensitisation
Link to relevant study records
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Dec 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Version / remarks:
- July 2010
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- Version / remarks:
- May 2008
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.2600 (Skin Sensitisation)
- Version / remarks:
- March 2003
- GLP compliance:
- yes (incl. QA statement)
- Type of study:
- mouse local lymph node assay (LLNA)
- Specific details on test material used for the study:
- TREATMENT OF TEST MATERIAL PRIOR TO TESTING
The test substance formulations (w/w) were prepared within 4 hours prior to each treatment. No adjustment was made for specific gravity of the vehicle. Homogeneity was obtained to visually acceptable levels. The formulations were stirtred with magnetic stirrer immediately prior to dosing. - Species:
- mouse
- Strain:
- other: CBA/J
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Janvier, Le Genest-Saint-Isle, France
- Females nulliparous and non-pregnant: yes
- Microbiological status of animals, when known: SPF
- Age at study initiation: approx. 11 weeks old
- Weight at study initiation:
- Housing: group housed
- Diet (e.g. ad libitum): pelleted rodent diet (SM R/M-Z from SSNIFF® Spezialdiäten GmbH, Soest, Germany), ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: at least 5 d
A health inspection was performed prior to treatment, to ensure that the animals were in a good state of health. Special attention was paid to the ears, which were intact and free from any abnormality.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21.0 ± 3.0ºC (actual range: 17.6 - 21.6ºC),
- Humidity (%): 40-70% (actual range: 21 – 64%)
- Air changes (per hr): approx 15
- Photoperiod (hrs dark / hrs light): 12/12 - Vehicle:
- propylene glycol
- Concentration:
- Pre-Screen test: 25% and 50%
Main test: 10%, 25% and 50% - No. of animals per dose:
- Pre-Screen test: 2
Main Test: 5 - Details on study design:
- PRE-SCREEN TESTS:
- tested at 25% and 50% concentration
- Compound solubility:
- Irritation: Slight irritation along with white test substance remnants (which did not hamper scoring) were observed on both ears of all animals treated at a 25 and 50% concentration between Days 1 and 3
- Systemic toxicity: no
- Ear thickness measurements: no
MAIN STUDY
- Criteria used to consider a positive response:
DPM values are presented for each animal and for each dose group. A Stimulation Index (SI) is calculated for each group. The SI is the ratio of the DPM/group compared to DPM/vehicle control group.
If the results indicate a SI ≥ 3, the test substance may be regarded as a skin sensitizer, based on the test guideline and recommendations done by ICCVAM.
TREATMENT PREPARATION AND ADMINISTRATION:
On the induction days 1,2 and 3 the dorsal surface of both ears was topically treated (25 µl/ear) with the test substance concentration.
On day 6 the draining (auricular) lymph node of each ear was excised after injection of 3H-methyl thymidine via tail vein to the mice 5 h before and tissue was processed for radioactivity measurements.
Additionally, clinical signs (daily), body weights (day 1 and 6) and signs of irritation or other local effects were observed. - Positive control substance(s):
- other:
- Positive control results:
- reliability check:
The SI values calculated for the substance concentrations 5, 10 and 25% were 1.2, 2.2 and 3.7 respectively. An EC3 value of 18.0% was calculated using linear interpolation.
The calculated EC3 value was found to be in the expected range of 2 and 20%. The results of 6 monthly HCA reliability checks of the recent years were 13.8, 13.9, 16.0, 11.9, 16.9 and 10.7%. - Parameter:
- SI
- Value:
- 1.6
- Variability:
- +- 0.4
- Test group / Remarks:
- 5 females/10 %-group
- Key result
- Parameter:
- SI
- Value:
- 1.7
- Variability:
- +- 0.5
- Test group / Remarks:
- 5 females/25 %-group
- Parameter:
- SI
- Value:
- 0.9
- Variability:
- +- 0.2
- Test group / Remarks:
- 5 females/50 %-group
- Parameter:
- SI
- Value:
- 1
- Variability:
- +- 0.2
- Test group / Remarks:
- vehicle control group
- Parameter:
- other: mean disintegrations per minute (DPM)/animal
- Value:
- 449
- Test group / Remarks:
- 10 %-group
- Parameter:
- other: mean disintegrations per minute (DPM)/animal
- Value:
- 470
- Test group / Remarks:
- 25 %-group
- Parameter:
- other: mean disintegrations per minute (DPM)/animal
- Value:
- 268
- Test group / Remarks:
- 50 %-group
- Parameter:
- other: mean disintegrations per minute (DPM)/animal
- Value:
- 283
- Test group / Remarks:
- vehicle control group
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- not skin sensitizing
- Executive summary:
To determine the skin-sensitizing properties of estrone the mouse local lymph node assay was performed on female CBA/J mice (5/group) according to OECD guideline 429. The main study was conducted with the following test substance concentrations: 0 (vehicle control), 10%, 25% and 50% formulated in propylene glycol.
All animals treated with 25 and 50% showed slight irritation of the ears, but this had no toxicological significant effect on the activity of the lymph nodes. White test substance remnants were present on the ears of all animals at 10, 25 and 50%, which did not hamper scoring of the skin irritation reactions.
All auricular lymph nodes of the animals of the experimental and control groups were considered normal in size. No macroscopic abnormalities of the surrounding area were noted in any of the animals.
Mean DPM/animal values for the experimental groups treated with test substance concentrations 10,
25 and 50% were 449, 470 and 268 DPM respectively. The mean DPM/animal value for the vehicle
control group was 283 DPM.The mean DPM/animal values were 283 (vehicle control), 449 (10%), 470 (25%) and 268 (50%). The SI values calculated were 1.6 (10%), 1.7 (25%) and 0.9 (50%). Since there was no indication that the test substance elicits an SI above or equal to 3 when tested up to 50%, estrone was considered not to be a skin sensitizer.
A regularly performed reliability check with Alpha-hexylcinnamicaldehyde indicates that the Local Lymph Node Assay as performed at the laboratory is an appropriate model for testing for contact hypersensitivity.
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- HYPOTHESIS FOR THE ANALOGUE APPROACH
Regarding human health, toxicity studies for estrone 3-methyl ether (estrone-3-methylether) and its structural relative estrone are available according to REACH requirements of Annex VII (1-10 t/a). The underlying mechanism linking these substances is the effect they exert on the estrogen receptor, although the potency is quantitatively somewhat different.
Estrone shows a pharmacological profile (comprising the binding to different hormone receptors) similar to estrone-3-methylether which suggests the comparison of the biological activity regarding human health toxicology of both substances after becoming systemically available and to justify the use of estrone as a source for read-across to estrone-3-methylether as target. Regarding the underlying biological mechanism of acting on the estrogen receptor estrone is more potent than estrone-3-methylether and can therefore be considered as a worst-case scenario.
The source substance estrone and the target substance estrone-3-methylether are structurally similar, moderately lipophilic substances, which are absorbed after administration and differently (bio)transformed but leading to the same final metabolites. The exposure to source and target substance causes the same type of effects through a common mechanism: induction of pharmacologic effects via the estrogen receptor.
The strength of effects of the source substance is predicted to be the worst-case scenario for the effects of the target substance for the property under consideration. The common metabolites (2- or 4-Hydroxyestrone-3-methyl ether) are assumed to be less biological active compared to estrone.
It is further assumed that the pharmacological effect dominates the biological activity of estrone-3-methylether and toxicological effects due to off-target binding are not anticipated below this pharmacological effect level.
Whereas estrone is an endogenous steroid hormone that can be (reversely) converted into estradiol and serves mainly as a precursor or metabolic intermediate of estradiol, estrone-3-methylether is a synthetic steroid hormone which is metabolized only into one direction but not reverse.
The read-across hypothesis is supported by the finding that CYP450-mediated metabolism of estrone and estrone-3-methylether was similar in rat liver microsomes in vitro.
In summary, it can be concluded that estrone and estrone-3-methylether exert very similar comparable biological effects in vivo via the estrogen receptor.
A detailed justification for read-across is attached on iuclid section 13. - Reason / purpose for cross-reference:
- read-across: supporting information
- Reason / purpose for cross-reference:
- read-across source
- Parameter:
- SI
- Value:
- 1.6
- Variability:
- +- 0.4
- Test group / Remarks:
- 5 females/10 %-group
- Parameter:
- SI
- Value:
- 1.7
- Variability:
- +- 0.5
- Test group / Remarks:
- 5 females/25 %-group
- Parameter:
- SI
- Value:
- 0.9
- Variability:
- +- 0.2
- Test group / Remarks:
- 5 females/50 %-group
- Parameter:
- SI
- Value:
- 1
- Variability:
- +- 0.2
- Test group / Remarks:
- vehicle control group
- Parameter:
- other: mean disintegrations per minute (DPM)/animal
- Value:
- 449
- Test group / Remarks:
- 10 %-group
- Parameter:
- other: mean disintegrations per minute (DPM)/animal
- Value:
- 470
- Test group / Remarks:
- 25 %-group
- Parameter:
- other: mean disintegrations per minute (DPM)/animal
- Value:
- 268
- Test group / Remarks:
- 50 %-group
- Parameter:
- other: mean disintegrations per minute (DPM)/animal
- Value:
- 283
- Test group / Remarks:
- vehicle control group
- Conclusions:
- not skin sensitizing
- Executive summary:
No data on sensitising properties is available for the target substance estrone-methylether. Results of a study conducted with estrone are regarded as representative based on close structural similarity as further detailed in the Justification for read-across attached to Iuclid section 13.
To determine the skin-sensitizing properties of estrone the mouse local lymph node assay was performed on female CBA/J mice (5/group) according to OECD guideline 429. The main study was conducted with the following test substance concentrations: 0 (vehicle control), 10%, 25% and 50% formulated in propylene glycol.
All animals treated with 25 and 50% showed slight irritation of the ears, but this had no toxicological significant effect on the activity of the lymph nodes. White test substance remnants were present on the ears of all animals at 10, 25 and 50%, which did not hamper scoring of the skin irritation reactions.
All auricular lymph nodes of the animals of the experimental and control groups were considered normal in size. No macroscopic abnormalities of the surrounding area were noted in any of the animals.
Mean DPM/animal values for the experimental groups treated with test substance concentrations 10, 25 and 50% were 449, 470 and 268 DPM respectively. The mean DPM/animal value for the vehicle control group was 283 DPM.The mean DPM/animal values were 283 (vehicle control), 449 (10%), 470 (25%) and 268 (50%). The SI values calculated were 1.6 (10%), 1.7 (25%) and 0.9 (50%). Since there was no indication that the test substance elicits an SI above or equal to 3 when tested up to 50%, estrone was considered not to be a skin sensitizer.
A regularly performed reliability check with Alpha-hexylcinnamicaldehyde indicates that the Local Lymph Node Assay as performed at the laboratory is an appropriate model for testing for contact hypersensitivity.
Based on read-across, estrone-methylether is not a skin sensitiser.
Referenceopen allclose all
No mortalities occurred, no symptoms of systemic toxicity, no changes in body weights and body weight gain were observed.
A slight irritation (grade 1) of the ears was seen in all animals treated with 25 and 50%, but this was considered not to have a toxicologically significant effect on the activity of the nodes. No oedema were observed.
All auricular lymph nodes were considered normal in size, no macroscopic abnormalities of the surrounding area were noted in any of the animals.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (not sensitising)
- Additional information:
With respect to skin sensitizing effects, no experimental study data for estrone-3-methylether is available. Read-across is applied using experimental in vivo data in mice (Local lymph node assay; LLNA according to OECD TG 429) with estrone as source. Substance purity of estrone in this guideline GLP study was >95% and reliability of the study report is allocated to Klimisch score 1.
To determine the skin-sensitizing properties of estrone the mouse local lymph node assay was performed on female CBA/J mice (5/group) according to OECD guideline 429. The main study was conducted with the following test substance concentrations: 0 (vehicle control), 10%, 25% and 50% formulated in propylene glycol.
All animals treated with 25 and 50% showed slight irritation of the ears, but this had no toxicological significant effect on the activity of the lymph nodes. White test substance remnants were present on the ears of all animals at 10, 25 and 50%, which did not hamper scoring of the skin irritation reactions.
All auricular lymph nodes of the animals of the experimental and control groups were considered normal in size. No macroscopic abnormalities of the surrounding area were noted in any of the animals.
Mean DPM/animal values for the experimental groups treated with test substance concentrations 10,
25 and 50% were 449, 470 and 268 DPM respectively. The mean DPM/animal value for the vehicle
control group was 283 DPM. The mean DPM/animal values were 283 (vehicle control), 449 (10%), 470 (25%) and 268 (50%). The SI values calculated were 1.6 (10%), 1.7 (25%) and 0.9 (50%). Since there was no indication that the test substance elicits an SI above or equal to 3 when tested up to 50%, estrone was considered not to be a skin sensitizer.
A regularly performed reliability check with Alpha-hexylcinnamicaldehyde indicates that the Local Lymph Node Assay as performed at the laboratory is an appropriate model for testing for contact hypersensitivity (van Otterdijk, 2011).
No sensitization potential for estrone was demonstrated in this study, i.e. no relevant increase in DPM and SI-values compared to controls up to the highest concentration used (50%). Slight and reversible local irritation of the skin after topical application of estrone to the murine ears in the 25% and 50% concentration groups did not result in any lymph node findings and was therefore not regarded as adverse effect related to the outcome of this study. Dermal absorption based on enhanced lipophilicity and logPow values of estrone and estrone-3-methylether is assumed to be similar for both substances therefore justifying a read-across approach for this particular endpoint. Further biological activity of both substances is due to the activation of the estrogen receptor with estrone (source) representing a worst-case scenario for estrone-3-methylether (target).
The experimental result for estrone is supported by the safe dermal application of other estrogens (in particular the more potent estradiol) in several clinical studies without adverse or sensitization findings (Rzepecki, 2019). For example, a 6-month topical treatment of 59 preclimateric women with skin-aging symptoms with 0.01% estradiol and 0.3% estriol compounds was was tolerated well without skin reactions (Schmidt, 1996). In general, the systemic absorption of local or topical estrogen therapies is thought to be quite low (Klinger, 2002). Although a clinical case study published in 1995 demonstrated increased sensitivity in 6 of 7 women after intradermal application (subepidermal injection of 0.1 ml) of estrogens including estrone (Shelley, 1995) this finding can be regarded as a very rare event.
In addition, an in silico assessment of skin sensitization (QSAR Toolbox 4.3.1) for estrone and estrone-3-methylether was carried out. For estrone the QSAR Toolbox reveals ‘Protein binding alerts for skin sensitisation by OASIS’ (identical with estrone-3-methylether) - but not ‘Protein binding alerts for skin sensitisation according to GHS’. Both profilers showed alerts for estrone-3-methylether. All alerts are based on the reactivity of the ketone group (addition to the carbon-hetero double bond) and no other skin sensitization profiler showed any alert. The negative experimental LLNA data for estrone indicate that under in vivo conditions no skin sensitization occurs in contrast to the positive QSAR alert.
The presence of a methoxy-group or hydroxyl-group in the molecule is regarded as not relevant for skin sensitization as these groups are not able for protein binding as a basic requirement for skin sensitization.
Further, the anticipated metabolism of estrone-3-methylether by enzymatic CYP450 degradation in the epidermis of the skin (refer to 4.2) resulting in the endogenous 2- or 4-Hydroxyestrone-3-methyl ether will not increase immunogenicity of the hapten. Consequently, estrone-3-methylether (CAS 1624-62-0) is concluded as not sensitizing.
Based on the LLNA data for estrone as read-across source and the comparison to the in silico prediction results for both substances no skin sensitizing potential can be concluded for estrone-3-methylether epicutaneously and therefore classification (Reg. (EC) No. 1272/2008) is not warranted.
QSAR predictions and LLNA sensitization of estrone for read-across to estrone-3-methylether
Estrone
Estrone-3-methylether
CAS No.
53-16-7
1624-62-0
ZK
5019
5512
QSAR prediction (Toolbox 4.3.1); Report Schlecker, 2019
Profilers with protein binding alerts for skin sensitization
1
(OASIS)
2
(OASIS & GHS)
Alerts
Nucleophilic addition/ Addition to Carbon-hetero double bonds/ Ketones
· Nucleophilic addition/ Addition to Carbon-hetero double bonds/ Ketones
· Skin sensitization Category 1B >> Ketones
LLNA study
Study no./ Report no.
NOTOX 495755
(Otterdijk, 2011)
No data
Read-across
GLP/ OECD TG/ deviations
GLP, OECD 429; no deviations
Regular reliability check with α-hexylcinnamic-aldehyde
Species; animals/ group
Mice, female n=5/ group (main study)
Compound purity/ formulation
· Batch EFB465K1A
· Purity >95%
· Vehicle: propylene glycol
· freshly prepared, homogeneity visually confirmed
Doses tested
10%, 25% and 50% w/w, dose selection based on pre-test
Route/ schedule
Topical treatment of ears on d1, d2 and d3
Parameters assessed
Skin reactions, auricular lymph node assessment, BW in comparison to vehicle, radioactivity measurements of activated LN cells, systemic toxicity
Results
no skin sensitization
Reliability
1
References:
Klinger W. et al., Toxicology Letters 128 (2002) 129–144
Rzepecki et al. Int J Womens Dermatol. 2019 Jun; 5(2): 85–90
Schmidt et al. 1996; Int J Dermatol Vol 35, No. 9, 669
Shelley et al. 1995, Journal of the American Academy of Dermatology, Volume 32, Issue 1, January 1995, Pages 25-31
Respiratory sensitisation
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
Based on the data for surrogate no classification for skin sensitisation according to Regulation (EC) No. 1272/2008 (CLP) is required for estrone methyl ether.
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